Total marine fisheries extractions by country in the Baltic Sea

Total marine fisheries extractions by country in the Baltic Sea Total marine fisheries extractions by country in the Baltic Sea

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166 Total marine fisheries extractions by country in the Baltic Sea: 1950-present, Rossing, Booth and Zeller fisheries. Deep-sea trawlers operate exclusively in the north Atlantic, east Atlantic, and Antarctic. Cutter vessels contribute approximately 88% of Polish reported landings in the Baltic, with coastal vessels (considered artisanal) contributing the remaining 12%. This report will address only those catches of coastal, cutter, and recreational fisheries in the Baltic, which operate mainly in ICES sub-divisions 24-26 (Figure 1). Overall, Poland obtains more than 80% of its reported landings from the Baltic (Anon., 2008). According to the International Council for the Exploration of the Sea (ICES, 2009a), Poland‘s landings are mainly comprised of three species: sprat (Sprattus sprattus); herring (Clupea harengus); and cod (Gadus morhua). Overall, Poland‘s landings increased steadily from the 1950s-1970s, experienced a brief decline through privatization of the industry in the 1990s, and increased slightly in the early 2000s. Table 1. ICES divisions and corresponding subdivisions representing the Danish Sound, Belt and Baltic Sea. Source: (ICES, 1987). ICES Division ICES Subdivision IIIb- Sound 23 IIIc- Belt Sea 22 IIId- Baltic Sea 24-32 Since Poland joined the EU in 2004, landings have declined overall for a number of reasons. These include the EU fleet capacity reduction programme, rising fuel costs, falling fish prices and decreasing shares of EU Total Allowable Catches (TACs) for cod; Poland‘s most economically important species. Since 2004, the entire Baltic fleet has been reduced from 1,374 vessels, to 866 vessels (Anon., 2006b; 2008). In 2005, reported landings of the cutter fleet consisted predominantly of sprat (68%), herring (17%), and cod (11%; FAO, 2009) which were caught with gillnets, hooks and trawls. Boats of the coastal fleet are generally less than 15 m, and primarily use gillnets within 12 nautical miles of the shore. The reported landings of these vessels in 2005 were cod (28%), flatfishes (27%), and herring (22%; FAO, 2009). Poland has a flounder-directed (Platichthys flesus) gillnet fishery which operates predominantly within ICES sub-division 25 (Figure 1; ICES, 2005b). Historically, all Polish landings were reported from ICES division IIId (prior to 1980). In 1978, reporting by ICES subdivision was initiated in the Baltic (ICES, 1995). ICES division IIId became equivalent to ICES subdivisions 24-32, which represents the Baltic Sea (Figure 1; Table 1). ICES divisions IIIb and IIIc are equivalent to ICES sub divisions 23 and 22, respectively (Figure 1; Table 1), and are collectively known as the ‗transition zone‘ between the Skagerrak and Baltic Sea (ICES, 1995). Since reporting by subdivision began, Poland has reported roughly equal landings from subdivisions 25 and 26 (about 45% of the Polish total in each) and a small portion (about 10%) in subdivision 24 (Table 2). In the 2000s, a very small amount of sprat was reported from subdivisions 27, 28 and 29 (Table 2). Table 2. Percent distribution of Poland‘s reported landings by ICES subdivision, by decade (1980-2007). Prior to 1980 all landings were reported from ICES division IIId. Data source: (ICES, 2009). Fishing area Reported landings (%) 1980-1989 1990-1999 2000-2007 ICES Division a IIId 37.0 n/a b n/a b ICES Subdivision 24 6.6 9.9 8.4 25 30.7 46.1 46.7 26 25.9 44.1 44.8 27 0.0 0.0 0.03 28 0.0 0.0 0.05 29 0.0 0.0 0.03 a historically, landings were reported by ICES division as opposed to subdivision. In 1978, reporting began by subdivision (ICES, 1987). Consequently, some reporting in the 1980s is by division and some by subdivision. b not-applicable. Sport and recreational fishing began in the late 1980s. It became more popular after 1993, when some fishers converted their commercial cutters into recreational tour boats fishing for cod (Radtke and Dabrowski, 2007). A severe lack of quantitative record exists, however a restrictive quota was created in 2004 to control angling of cod to some extent. An initiative to distribute public surveys seeks to obtain further information regarding recreational fishing activities (ICES, 2005a). Before 1989, Poland administered the regulations of the Baltic Sea Commission (CPMR), and all fish sold on local markets were distributed through the government-owned company, Centrala Rybna. All exports and imports were managed by Rybex, which was also government-owned. Privatization of the fishing industry reduced the number of nationally owned vessels from 226 in the early 1990s, to 8 in 2006. Though privatization in the 1990s had seemingly little effect on reported landings, IUU (Illegal, Unreported and Unregulated fishing) were reportedly non-existent in Poland prior to the early 1990s

Total marine fisheries extractions by country in the Baltic Sea: 1950-present, Rossing, Booth and Zeller 167 (Anon., pers. comm.). 2 Historically, fishers had strict quotas and were required to land their catches along with detailed reports at national collection points. Fishers were thus unable to sell directly to the market, which made IUU fishing unprofitable (Anon., pers. comm.). Poland joined the EU in 2004 and became subject to the rules of the Common Fisheries Policy (CFP). This included a reduction in fleet capacity and a new TAC system which consequently, made over-fishing and underreporting very economical for private fishers, and especially those targeting cod. The EU commission banned Poland from cod fishing after discovering one particular fisher had registered only 1/3 of cod landings in the first semester of 2007 (Anon., pers. comm.). The country is now being forced to make up for underreported landings with additional reductions to Poland‘s current share of the TAC for cod. ICES estimates underreporting in the Polish cod fishery ranges between 35-45% (Anon., pers. comm.), the World Wildlife Fund 50% (Anon., 2009b), and an estimate of more than 300% was obtained from a highly reliable anonymous source interviewed in 2008. In the first half of the 1970s, Poland‘s cod fishery was one of the most important of its kind in the Baltic. Polish landings accounted for 30% of the total cod landings from the Baltic, and about 38% of these were taken from the eastern stock (Subdivisions 25-32; ICES, 1995). These stocks are now considered to be in the worst condition of any cod in the Baltic, and thus the majority of Poland‘s management schemes are concerned with the conservation of this species. Minimum mesh size, landing size, closed areas and seasons are being used as current management controls on cod fishing. The introduction of the Bacoma trawl in 2004 has also helped to reduce bycatch of juvenile cod (FAO, 2007). Polish fishers have displayed very strong opposition to fishing bans as well as the repercussions associated with unregulated and underreported fishing. They argue that even with increased individual fishing quotas, the reduction in fleet capacity in combination with low overall TACs for commercial species, and high fuel prices have made fishing unprofitable. Although Poland‘s share of EU quotas for cod have been exceeded consistently since 2004, their TACs for herring and sprat are often left unfulfilled (up to 50%). This is due to the low prices for herring and sprat in comparison to cod, as well as the increased imports from countries such as Norway. Despite these drawbacks to marine fisheries, the processing sector in Poland has grown consistently since 2004 (FAO, 2009). The purpose of this study is to provide an estimate of Poland‘s total fisheries catches (in contrast to reported landings) in the Baltic Sea from 1950-2007. The ‗ICES catch statistics database‘ provides landings data for Poland from 1955-2007 (ICES, 2009a). These data are reported landings only, with no apparent effort to fully represent the total catch (which would account for IUU as well as reported landings). Therefore, for the purposes of this report the ICES catch statistics will be referred to as ICES ‗landings statistics‘ to better reflect the nature of the data. Estimates of IUU in this study include data source adjustments to reported landings, unreported (referred to as ‗unallocated‘ by ICES) landings, discards, and recreational catches. Our approach utilizes previously reported data by ICES, a review of the academic and grey literature, as well as correspondence with local experts. Our correspondence with local authorities entailed high degrees of desired anonymity by those interviewed. We would like to acknowledge those who provided information despite the risks involved pertaining to job security in the politically charged atmosphere which surrounds the topic of IUU and other controversial fisheries issues. METHODS The ‗ICES Catch Statistics database‘ (ICES, 2009a), is the only publicly available resource available that presents annual landings data for all taxa and all fishing areas within the Baltic Sea. For the purposes of our catch reconstruction, we referred to the ICES catch statistics as the ‗ICES landings statistics‘, which reflects the true nature of the data presented (i.e., the database presents ‗reported landings’, not total catches). Thus, ICES landings statistics provided the official baseline for our reconstruction to which 4 categories of Illegal, Unreported and Unregulated (IUU) catches were added to estimate total catch: i) ‗adjustments‘, being positive or negative additions to reported data, based on reputable ICES stock assessment working group data (ICES, 2009b), as well as national datasets; ii) ‗unreported’ landings (referred to by ICES as ‗unallocated‘ catches) being catches taken but not reported to officials; iii) ‗discards‘, being fish caught and disposed of at sea; and iv) ‗recreational catches’. Adjustments to reported landings provided the best estimate of commercial landings in Poland from 1950-2007, to which estimates of unreported landings, discards and recreational catches were added. When sufficient data to derive 2 Many sources interviewed for or interacted with in this report expressed a strong desire to remain anonymous for personal reasons.

<strong>Total</strong> <strong>mar<strong>in</strong>e</strong> <strong>fisheries</strong> <strong>extractions</strong> <strong>by</strong> <strong>country</strong> <strong>in</strong> <strong>the</strong> <strong>Baltic</strong> <strong>Sea</strong>: 1950-present, Ross<strong>in</strong>g, Booth and Zeller 167<br />

(Anon., pers. comm.). 2 Historically, fishers had strict quotas and were required to land <strong>the</strong>ir catches along<br />

with detailed reports at national collection po<strong>in</strong>ts. Fishers were thus unable to sell directly to <strong>the</strong> market,<br />

which made IUU fish<strong>in</strong>g unprofitable (Anon., pers. comm.). Poland jo<strong>in</strong>ed <strong>the</strong> EU <strong>in</strong> 2004 and became<br />

subject to <strong>the</strong> rules of <strong>the</strong> Common Fisheries Policy (CFP). This <strong>in</strong>cluded a reduction <strong>in</strong> fleet capacity and a<br />

new TAC system which consequently, made over-fish<strong>in</strong>g and underreport<strong>in</strong>g very economical for private<br />

fishers, and especially those target<strong>in</strong>g cod. The EU commission banned Poland from cod fish<strong>in</strong>g after<br />

discover<strong>in</strong>g one particular fisher had registered only 1/3 of cod land<strong>in</strong>gs <strong>in</strong> <strong>the</strong> first semester of 2007<br />

(Anon., pers. comm.). The <strong>country</strong> is now be<strong>in</strong>g forced to make up for underreported land<strong>in</strong>gs with<br />

additional reductions to Poland‘s current share of <strong>the</strong> TAC for cod. ICES estimates underreport<strong>in</strong>g <strong>in</strong> <strong>the</strong><br />

Polish cod fishery ranges between 35-45% (Anon., pers. comm.), <strong>the</strong> World Wildlife Fund 50% (Anon.,<br />

2009b), and an estimate of more than 300% was obta<strong>in</strong>ed from a highly reliable anonymous source<br />

<strong>in</strong>terviewed <strong>in</strong> 2008.<br />

In <strong>the</strong> first half of <strong>the</strong> 1970s, Poland‘s cod fishery was one of <strong>the</strong> most important of its k<strong>in</strong>d <strong>in</strong> <strong>the</strong> <strong>Baltic</strong>.<br />

Polish land<strong>in</strong>gs accounted for 30% of <strong>the</strong> total cod land<strong>in</strong>gs from <strong>the</strong> <strong>Baltic</strong>, and about 38% of <strong>the</strong>se were<br />

taken from <strong>the</strong> eastern stock (Subdivisions 25-32; ICES, 1995). These stocks are now considered to be <strong>in</strong><br />

<strong>the</strong> worst condition of any cod <strong>in</strong> <strong>the</strong> <strong>Baltic</strong>, and thus <strong>the</strong> majority of Poland‘s management schemes are<br />

concerned with <strong>the</strong> conservation of this species. M<strong>in</strong>imum mesh size, land<strong>in</strong>g size, closed areas and<br />

seasons are be<strong>in</strong>g used as current management controls on cod fish<strong>in</strong>g. The <strong>in</strong>troduction of <strong>the</strong> Bacoma<br />

trawl <strong>in</strong> 2004 has also helped to reduce <strong>by</strong>catch of juvenile cod (FAO, 2007). Polish fishers have displayed<br />

very strong opposition to fish<strong>in</strong>g bans as well as <strong>the</strong> repercussions associated with unregulated and<br />

underreported fish<strong>in</strong>g. They argue that even with <strong>in</strong>creased <strong>in</strong>dividual fish<strong>in</strong>g quotas, <strong>the</strong> reduction <strong>in</strong> fleet<br />

capacity <strong>in</strong> comb<strong>in</strong>ation with low overall TACs for commercial species, and high fuel prices have made<br />

fish<strong>in</strong>g unprofitable. Although Poland‘s share of EU quotas for cod have been exceeded consistently s<strong>in</strong>ce<br />

2004, <strong>the</strong>ir TACs for herr<strong>in</strong>g and sprat are often left unfulfilled (up to 50%). This is due to <strong>the</strong> low prices<br />

for herr<strong>in</strong>g and sprat <strong>in</strong> comparison to cod, as well as <strong>the</strong> <strong>in</strong>creased imports from countries such as<br />

Norway. Despite <strong>the</strong>se drawbacks to <strong>mar<strong>in</strong>e</strong> <strong>fisheries</strong>, <strong>the</strong> process<strong>in</strong>g sector <strong>in</strong> Poland has grown<br />

consistently s<strong>in</strong>ce 2004 (FAO, 2009).<br />

The purpose of this study is to provide an estimate of Poland‘s total <strong>fisheries</strong> catches (<strong>in</strong> contrast to<br />

reported land<strong>in</strong>gs) <strong>in</strong> <strong>the</strong> <strong>Baltic</strong> <strong>Sea</strong> from 1950-2007. The ‗ICES catch statistics database‘ provides<br />

land<strong>in</strong>gs data for Poland from 1955-2007 (ICES, 2009a). These data are reported land<strong>in</strong>gs only, with no<br />

apparent effort to fully represent <strong>the</strong> total catch (which would account for IUU as well as reported<br />

land<strong>in</strong>gs). Therefore, for <strong>the</strong> purposes of this report <strong>the</strong> ICES catch statistics will be referred to as ICES<br />

‗land<strong>in</strong>gs statistics‘ to better reflect <strong>the</strong> nature of <strong>the</strong> data. Estimates of IUU <strong>in</strong> this study <strong>in</strong>clude data<br />

source adjustments to reported land<strong>in</strong>gs, unreported (referred to as ‗unallocated‘ <strong>by</strong> ICES) land<strong>in</strong>gs,<br />

discards, and recreational catches. Our approach utilizes previously reported data <strong>by</strong> ICES, a review of <strong>the</strong><br />

academic and grey literature, as well as correspondence with local experts. Our correspondence with local<br />

authorities entailed high degrees of desired anonymity <strong>by</strong> those <strong>in</strong>terviewed. We would like to<br />

acknowledge those who provided <strong>in</strong>formation despite <strong>the</strong> risks <strong>in</strong>volved perta<strong>in</strong><strong>in</strong>g to job security <strong>in</strong> <strong>the</strong><br />

politically charged atmosphere which surrounds <strong>the</strong> topic of IUU and o<strong>the</strong>r controversial <strong>fisheries</strong> issues.<br />

METHODS<br />

The ‗ICES Catch Statistics database‘ (ICES, 2009a), is <strong>the</strong> only publicly available resource available that<br />

presents annual land<strong>in</strong>gs data for all taxa and all fish<strong>in</strong>g areas with<strong>in</strong> <strong>the</strong> <strong>Baltic</strong> <strong>Sea</strong>. For <strong>the</strong> purposes of<br />

our catch reconstruction, we referred to <strong>the</strong> ICES catch statistics as <strong>the</strong> ‗ICES land<strong>in</strong>gs statistics‘, which<br />

reflects <strong>the</strong> true nature of <strong>the</strong> data presented (i.e., <strong>the</strong> database presents ‗reported land<strong>in</strong>gs’, not total<br />

catches). Thus, ICES land<strong>in</strong>gs statistics provided <strong>the</strong> official basel<strong>in</strong>e for our reconstruction to which 4<br />

categories of Illegal, Unreported and Unregulated (IUU) catches were added to estimate total catch: i)<br />

‗adjustments‘, be<strong>in</strong>g positive or negative additions to reported data, based on reputable ICES stock<br />

assessment work<strong>in</strong>g group data (ICES, 2009b), as well as national datasets; ii) ‗unreported’ land<strong>in</strong>gs<br />

(referred to <strong>by</strong> ICES as ‗unallocated‘ catches) be<strong>in</strong>g catches taken but not reported to officials; iii)<br />

‗discards‘, be<strong>in</strong>g fish caught and disposed of at sea; and iv) ‗recreational catches’. Adjustments to reported<br />

land<strong>in</strong>gs provided <strong>the</strong> best estimate of commercial land<strong>in</strong>gs <strong>in</strong> Poland from 1950-2007, to which estimates<br />

of unreported land<strong>in</strong>gs, discards and recreational catches were added. When sufficient data to derive<br />

2<br />

Many sources <strong>in</strong>terviewed for or <strong>in</strong>teracted with <strong>in</strong> this report expressed a strong desire to rema<strong>in</strong> anonymous for personal reasons.

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